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Sedimentation velocity of morphologically diverse macrophytes and plastic particles

The dataset contains sedimentation velocity measurements for 22 morphologically diverse macroalgae species (n = 49), the seagrass Zostera marina (n = 3), and plastic particles of four distinct shapes (n = 16). Each sample was measured at least five times, with some measured up to seven times. Detailed morphological descriptions and images are available in the corresponding paper. Samples with a SampleID starting with "K" were collected in January 2023 from the Kiel Fjord, Germany (between Strande and Bülk light house, 54°26'57.4N 10°11'37.6E). U. gigantea was collected in June 2024 in Yerseke, Netherlands (51°30'09.0N, 4°02'39.7E). All other samples were collected in June 2024 at the same site from the Kiel Fjord as in 2023, as well as two additional locations (Schilksee, 54°25'16.3N 10°10'43.1E and Mönkeberg, 54°21'20.92N 10°10'41.97E). Sedimentation velocity measurements were conducted in plastic cylinders, allowing particles to sink 15 cm to reach their terminal sinking velocity before starting the measurements. The sinking time was recorded using a stopwatch, and sedimentation velocity was calculated by dividing the sinking distance by the elapsed time. Test with varying cylinder heights showed no significant differences in results. Macrophyte species measured: Fucus vesiculosus, Fucus serratus, Saccharina latissima, Gracilaria vermiculophylla, Ceramium virgatum, Vertebrata fucoides, Polysiphonia stricta, Spermothamnion repens, Ahnfeltia plicata, Furcellaria lumbricalis, Coccotylus truncatus, Delesseria sanguinea, Cladophora flexuosa, Cladophora sp., Rhodomela confervoides, Pyropia leucosticta, Ulva clathrata, Ulva linza, Kornmannia leptoderma, Bryopsis hypnoides, Acrosiphonia centralis, Ulva gigantea, and Zostera marina. The plastic particles include eight circular pieces of foil (disks), three table tennis balls, two plastic nets, and three rubber bands. The foil disks were cut to different diameters and some were punched with different numbers of small holes. The name of the foil circles indicates both their diameter and perforation level. For example, "Disk 40-1" had a diameter of 40 mm and was unpunched, where "1" denotes unpunched, "2" partially punched, and "3" heavily punched, "4" extremely heavily punched. The three tennis balls shared identical dimensions but had different mass densities due to the different level of replacement of air with seawater and glass beads in the tennis ball.

Bebauungsplaene Gersheim/Bliesdalheim - Zum Rech 1. Änderung (OT Bliesdalheim)

Bebauungspläne und Umringe der Gemeinde Gersheim (Saarland), Ortsteil Bliesdalheim:Bebauungsplan "Zum Rech 1. Änderung (OT Bliesdalheim)" der Gemeinde Gersheim, Ortsteil Bliesdalheim

Bebauungsplaene Saarlouis/Beaumarais - Am Rech Nr.64_0

Bebauungspläne und Umringe der Kreisstadt Saarlouis (Saarland) Stadtteil Beaumarais:Bebauungsplan "Am Rech Nr.64_0" der Kreisstadt Saarlouis, Stadtteil Beaumarais

Bebauungsplaene Gersheim/Bliesdalheim - Zum Rech

Bebauungspläne und Umringe der Gemeinde Gersheim (Saarland), Ortsteil Bliesdalheim:Bebauungsplan "Zum Rech" der Gemeinde Gersheim, Ortsteil Bliesdalheim

An integrated multiple driver mesocosm experiment reveals the effect of global change on planktonic food web structure

We conducted a mesocosm experiment with an integrated multiple driver design to assess the impact of future global change scenarios on plankton, a key component of marine food webs. The experimental treatments were based on the RCP 6.0 and 8.5 scenarios developed by the IPCC, which were Extended (ERCP) to integrate the future predicted changing nutrient inputs into coastal waters. The mesocosm experiment was conducted over three weeks in late-summer (August-September) 2018. Seawater containing a natural plankton community was collected from the coastal North Sea. At the onset of the experiment, CO2 saturated seawater was added to the ERCP scenario mesocosms to adjust pCO2 and pH levels for each scenario. To create a realistic environment, we also manipulated the atmospheric pCO2 in the enclosed mesocosm tanks throughout the experiment. Seawater temperature was adjusted daily according to the current North Sea temperature measured at the Helgoland Roads for the Ambient, and 1.5°C and 3.0°C warmer for the ERCP 6.0 and ERCP 8.5 scenarios, respectively. Dissolved nutrient concentrations were determined at the onset of the experiment and adjusted to reach the desired N:P ratios. Samples were taken in an interval of 1-3 days depending on the phytoplankton bloom development, and community composition, except for the large mesozooplankton, was monitored throughout the experiment period.

CTD (AWI 1413, Sea & Sun 90 M Series II) data collected during the DAUNE experiment near Helgoland in August 2020

This data set contains CTD data collected during the DAUNE experiment using the given sensor. The goal of this experiment was to reach a common understanding of how measurement uncertainty can be derived initially focusing on temperature data. Data collection was performed using the AWI O2A infrastructure (https://epic.awi.de/id/eprint/37171/) which performs automatized near real time quality control. During the data ingest and archival process, the hereby assigned quality flags used by the O2A system have been transformed into the pangaea flagging scheme as follows, flagging symbols are shown in brackets: O2A Flag ->PANGAEA Flag No quality control (0) ->unknown (*) Good data (1) ->valid () Probably good (2) ->questionable (?) Probably bad (3) ->questionable (?) Bad (4) ->not valid (/)

CTD (AWI 1413, Sea & Sun 90 M Series II) data collected during the DAUNE experiment near Helgoland in July 2020

This data set contains CTD data collected during the DAUNE experiment using the given sensor. The goal of this experiment was to reach a common understanding of how measurement uncertainty can be derived initially focusing on temperature data. Data collection was performed using the AWI O2A infrastructure (https://epic.awi.de/id/eprint/37171/) which performs automatized near real time quality control. During the data ingest and archival process, the hereby assigned quality flags used by the O2A system have been transformed into the pangaea flagging scheme as follows, flagging symbols are shown in brackets: O2A Flag ->PANGAEA Flag No quality control (0) ->unknown (*) Good data (1) ->valid () Probably good (2) ->questionable (?) Probably bad (3) ->questionable (?) Bad (4) ->not valid (/)

CTD (MARUM 13894, SBE 37) data collected during the DAUNE experiment near Helgoland

This data set contains CTD data collected during the DAUNE experiment using the given sensor. The goal of this experiment was to reach a common understanding of how measurement uncertainty can be derived initially focusing on temperature data. Data collection was performed using the AWI O2A infrastructure (https://epic.awi.de/id/eprint/37171/) which performs automatized near real time quality control. During the data ingest and archival process, the hereby assigned quality flags used by the O2A system have been transformed into the pangaea flagging scheme as follows, flagging symbols are shown in brackets: O2A Flag ->PANGAEA Flag No quality control (0) ->unknown (*) Good data (1) ->valid () Probably good (2) ->questionable (?) Probably bad (3) ->questionable (?) Bad (4) ->not valid (/)

EU-Chemikalienverordnung REACH

Seit 1. Juni 2008 gilt die neue EU-Chemikalienverordnung REACH in ihren wesentlichen Teilen. REACH steht für Registration, Evaluation, Authorisation and Restriction of Chemicals. Alle Stoffe, welche in Mengen ab 1 Jahrestonne herstellt oder in den Verkehr gebracht werden, unterfallen danach einer Registrierpflicht. Die Registrierung von Stoffen ist bei der Europäischen Chemikalienagentur in Helsinki (ECHA) vorzunehmen.

Überarbeitung der statistischen Guidance zu OECD Prüfrichtlinien (OECD Series on Testing and Assessment No. 54)

Hintergrund: Datenanforderungen der Europäischen Verordnungen für Industriechemikalien (REACH 1907/2006/EG), Pflanzenschutzmittel (1107/2009/EG), Biozide (528/2012/EG), Tierarzneimittel (2019/6/EG) und der Richtlinie für Arzneimittel (2004/28/EG und 2004/27/EG) basieren auf standardisierten ökotoxikologischen Labor- und Freilandtests., i.d.R. OECD-Prüfrichtlinien. Die Festlegung der statistischen Auswertung der Labordaten erfolgt derzeit in den einzelnen OECD-Prüfrichtlinien mit Hinweis auf die 2006 veröffentlichten Grundprinzipien der statistischen Auswertung für OECD-Prüfrichtlinien im OECD Dokument Nr. 54 'Current approaches in the statistical analysis of ecotoxicity data: a guidance to application'. Die im OECD Dokument Nr. 54 beschriebenen Methoden sind (teilweise) überholt und es fehlen geeignete Methoden für die Auswertung von nicht-normalverteilten Daten. Nicht-normalverteilte Daten kommen standardmäßig in aquatischen Mesokosmen und Freilandstudien an Bodenorganismen und Arthropoden vor, die eine zentrale Rolle in der Zulassung von Chemikalien spielen. Eine Überarbeitung des OECD Dokuments Nr. 54 ist dringend notwendig, weil es direkte Auswirkungen auf die statistische Auswertung aller OECD-Prüfrichtlinien für die Bewertung von Auswirkungen auf Nichtzielorganismen hat. Forschungsziele sind: 1. Aktualisierung von OECD Dokument Nr. 54 - Aufnahme fehlender Methoden-Prüfung und Aktualisierung enthaltener Methoden, 2. Überführung des OECD Dokument Nr. 54 in ein OECD Guidance Dokument (verbindlicher) - Ermöglichung direkter Verweise zu bestehenden OECD-Prüfrichtlinien und der Vereinheitlichung statistischer Verfahrensweisen innerhalb bestehender OECD Prüfrichtlinien sowie eine präzisierte Ableitung der abgeleiteten Endpunkte zur Verbesserung der Risikobewertung für Chemikalien.

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